US2428328A - Process of removing bacteria from fluids - Google Patents

Process of removing bacteria from fluids Download PDF

Info

Publication number
US2428328A
US2428328A US457522A US45752242A US2428328A US 2428328 A US2428328 A US 2428328A US 457522 A US457522 A US 457522A US 45752242 A US45752242 A US 45752242A US 2428328 A US2428328 A US 2428328A
Authority
US
United States
Prior art keywords
bacteria
column
vessel
water
granular
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
US457522A
Inventor
Ham Garnet Philip
Barnes Robert Bowling
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Wyeth Holdings LLC
Original Assignee
American Cyanamid Co
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by American Cyanamid Co filed Critical American Cyanamid Co
Priority to US457522A priority Critical patent/US2428328A/en
Application granted granted Critical
Publication of US2428328A publication Critical patent/US2428328A/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/46109Electrodes
    • C02F1/46114Electrodes in particulate form or with conductive and/or non conductive particles between them
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection

Definitions

  • This invention relates to the removal of bacteria from uid media.
  • An object of our invention is to provide a. method of purifying fluids contaminated with bacteria by removing the bacteria from the fluids.
  • Another object of our invention is to provide fluids, particularly water, having a very low or substantially no bacterial content.
  • a fluid medium containing bacteria or the like with a relatively inert, dielectric material which has been or which is subjected to a source of high potential, direct current electricity.
  • a fluid such as water containing bacteria
  • a bed or column or a granular dielectric material to which is applied a high tension direct current by means of suitable electrodes.
  • These electrodes are conveniently located at the top and bottom of the bed or column of the granular material.
  • the dielectric material may be in the form of pellets, rods, tubes, etc., as Well as in the granular form.
  • Figure 2 is the same type view as Figure 1 but is a slightly different form of apparatus which is adapted for our process.
  • a suitable vessel or container I is preferably constructed of glass, porcelain or, if constructed with metal, it is preferably lined with glass, rubber or porcelain.
  • An electrode, preferably a platinum electrode, 3 is placed near the top of vessel I and it extends either a short distance or substantially entirely across the vessel.
  • a similar electrode 5 is inserted near the bottom of the vessel I.
  • the electrodes 3 and 5 are suitably insulated from the vessel I if the latter is metallic.
  • a high tension direct current potential is applied to the electrodes. 3 and 5 by any suitable means.
  • the electrode near the top of the vessel I is made the anode while the electrode near the bottom of the vessel I is made the cathode.
  • the electrodes 3 and 5 may be in the form of a wire or rod, or they may be in the form of a screen or foraminous plate which partly or completely covers the horizontally cross sectional area of the vessel I.
  • a feed conduit 1 is connected into the top of vessel I while an outlet conduit 9 is connected into the bottom of vessel I. Both conduits 'I and 9 may be constructed of materials similar to those specified for vessel I.
  • a relatively thin layer of glass Wool II may be placed in the bottom of the vessel I and on top of the glass wool a granular material I3 is well packed in order to avoid the channeling of the fluid passing through the apparatus. On the top of the granular material I3 another layer of glass wool I5 is placed and this in turn is followed by a layer of glass beads I1. Optionally, an overflow pipe I9 is connected intothe top of the vessel I.
  • Water or other iiuid containing bacteria flows in through conduit l down through the granular material in vessel I and out through conduit 9. During the passage of the water a high tension direct current potential is applied to electrodes 3 and 5. The eiliuent flowing from conduit 9 has a substantially lower bacterial content than the feed which ilows'in through conduit l.
  • container I is shown as a relatively shallow vessel as compared to vessel I, Figure 1 where the vessel is represented as a relatively long column.
  • the feed pipe 'l in Figure 2 is connected with a perforated distributor conduit 8 which may be formed into a circle.
  • the container I is provided with an ,outlet conduit 9.
  • electrodes 2I and 23 are inserted into the side of container I preferably diametrically opposite each other.
  • a supporting screen, grate or other foraminous support is placed in the bottom of container i.
  • On top of the support 25 a layer or glass wool li is placed followed by ⁇ well packed granular material i8 and this in turn is followed by another layer of glass wool Il on top of which is a layer of glass beads Il.
  • the container I conduits 1, I, and l and support 2l may be constructed of metal. porcelain. glass, synthetic resin. or many other 'desired materials. If metal be used, it is preferable that it be lined with glass, porcelain or rubber.
  • Example 1 A glass column about V4" in diameter and 24" long is provided with two platinum electrodes about 19" apart. Each electrode consists of No. 22 gauge platinum wire and extends inside of the glass column a distance of about t". The electrodes are preferably relatively small in order to reduce the current density in the column as much as possible. Since our invention deals with the application of the high potential to the column of granular material but not to the passage of high currents of electricity: through the column, it is to be noted that the current density employed according to our invention is insumcient to actually kill the bacteria.
  • the top electrode is the anode although our invention contemplates the use of the anode at either the bottom or top of the column.
  • the anode at or near the top of the column as somewhat better results are obtained than if the positions of the anode and cathode be reversed. This is of course based upon the direction of iiow being from top to bottom. We have found that the number of bacteria appears to be considerably greater in the vicinity of the anode than at the cathode.
  • the glass column is packed with a granular material such as flne sea sand.
  • the sea sand used in the following test was such that 98% by weight was within the range of No, 20 to 100 mesh.
  • the sand is washed and ignited prior to being packed in the column. Just prior to the introduction of the sand into the column it is washed with distilled water until the pH of the eiiiuent is about 6.8 at 25 C.
  • the entire apparatus is preferably steam sterilized at about 121 C. either before cr after the sand is placed in the column. sterilized water is passed through the sand to wash out any free contaminating material or free bacteria.
  • Samples of sand from three diiferent locations in the column were removed after the foregoing tests.
  • the first portion was taken from the vicinity of the anode at the top of the column.
  • the second portion was taken from the center of the column while the third portion was taken from the bottom of the column in the vicinity of the cathode.
  • One gram of each sample was slurried in a 5 cc. portion of sterile water and the sand allowed to settle. After settling, 1 cc. of the water in every sample was pipetted out, diluted 1:100 and a 0.1 cc. portion used for plating purposes.
  • a bacteriological examination showed that the first sample contained about 6,000,000 colonies per cc. of the water into which the sand was slurried.
  • Example 2 A bacterial suspension of pyocyaneous containing about 320,000 colonies per cc. is passed through a column of sand prepared in accordance with Example 1. About 1 liter of the suspension is passed through it at a rate oi' about 14 cc. per minute and the eilluent is collected in about' 100 cc. fractions. These were diluted, in-
  • Such granular materials should be nonconductors or poor conductors of electricity, or, in other words, they should be dielectrics. Such materials should have a resistivity of at least 100,000 ohms/cm. cube.
  • the granular materials should be substantially insoluble in the fluid to be treated, e. g., water, and they should be relatively rigid, that is to say, the particles should not collapse or ooalesce to form a mush or paste.
  • the materials have at least some degree of porosity, that they be water resistant, and that they be wet readily by water or other iluids to be purified. In view of these requirements it is apparent that we can not employ metals in their free state for our purpose.
  • substances which we may use are bauxite, calcium carbonate, calcium sulfate, aluminum oxide in any form, barium sulfate, magnesium carbonate, silicon carbide, calcium phosphate, the natural clays, quartz, glass, silica gels, diatomaceous earth, sodium aluminum silicate and other complex aluminum silicates,
  • a valuable feature of our invention is that the bacteria remain in contact with the granular material in a virulent condition.
  • the bacteria may be removed from the granular material by washing with water or other fluids and if de sired they may be killed or rendered inactive by treating them with germicidal solutionsor bacteriostatic solutions or subjecting them to a high potential, high frequency discharge by subjecting them to ultra-violet radiations, etc.
  • bacteria may be collected for use in the preparation of biologicals or for use in scientific studies.
  • the former may be agitated in a suitable vessel with a sufficient quantity of the granular material to achieve the desired result, said vessel containing electrodes to which va high potential is applied, or said granular material may have been previously subjected to a high electrical potential.
  • a suitable vessel with a sufficient quantity of the granular material to achieve the desired result
  • said vessel containing electrodes to which va high potential is applied, or said granular material may have been previously subjected to a high electrical potential.
  • any number of beds of granular material as well' as ⁇ dielectric material is preferably from about volts D. C. to about 2000 volts D. C. and even higher voltages may be employed if desired.
  • the current density is preferably kept as low as possible in order to avoid undesired decomposition of any salts which may be present in the :duid medium or of the uid medium itself. Furthermore, if it be desirable to recover the bacteria. in a virulent condition, the current density should not be high enough to kill the bacteria.
  • Our invention is not limited to the purication of liquids such as water, but is applicable to the puriilcation of any liquid or gas.
  • gases such as for example, air
  • the granular material be maintained in a damp or a wet condition, thus for example, air may be bubbled through a column packed with granular material through which a high potential electrical current is applied either with the column being kept substantially full oi' water or with water trickling or being sprayed down over the surface of the granular material. Gases may also be passed over the granular material after rst being saturated with water vapor.
  • a process for removing bacteria from aqueous media which comprises activating a granular dielectric material by applying a direct electric current potential of about 100-2000 volts thereto, in the presence of an aqueous liquid by means of electrodes oi such size and so spaced that the current passing between such electrodes when liquid is present is insuilicient to kill bacteria in said last-mentioned liquid, and passing an aqueous medium containing bacteria through a bed of the resulting activated dielectric material.
  • a process as in claim 2 wherein the granular dielectric material is sand.
  • a process which comprises passing an aqueous medium containing bacteria through a bed of a granular dielectric material which is activated by applying a direct electric current potential oi' about 10G-2000 volts thereto, by means of electrodes of such size and so spaced that the current passing between such electrodes when said aqueous media is present is insumcient to kill bacteria in said liquid, and collecting at least a portion of the eilluent which contains a lower concentration of bacteria than said medium.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Description

sept. 3o, 1947. G. P. Hmm AL 2,428,328
PROCESS OF REMOVING BACTERIA FROM FLUIDS Filed Sept. 5, 1942 3 a l S ATTORNEY Patented Sept. 30, 1947 PROCESS F REMOVING BACTERIA FROM FLUIDS Garnet Philip Ham, Old Greenwich, and Robert Bowling Barnes, Stamford, Conn., asslgnors to American Cyanamid Company, New York, N. Y., a corporation of Maine Application September 5, 1942, Serial No. 457,522
Claims. l
This invention relates to the removal of bacteria from uid media.
Many uids such as water are often contaminated with harmful bacteria to such an extent that they can not be safely used for food, beverages or medicinal'purposes.
Many methods of killing bacteria have been proposed and a few of them have found wide application. None of the methods of killing bacteria which have been employed prior to our invention are completely satisfactory for all purposes and in all instances. Some methods do not kill with sufficient efficiency while other methods are too slow to be practical. Furthermore, many of the prior art methods of killing bacteria involve the introduction of a toxic material such as chlorine to the fluid medium to be purified. Water treated with chlorine has an undesirable flavor and many people risk disease rather than use the distasteful chlorine in their drinking water.
An object of our invention is to provide a. method of purifying fluids contaminated with bacteria by removing the bacteria from the fluids.
Another object of our invention is to provide fluids, particularly water, having a very low or substantially no bacterial content.
In the eld of biologicals it is often desirable to concentrate bacteria and the like or to remove the bacteria fromthe media in which they are found in order to transfer them into another desired medium.
It is, therefore, another object of our invention to provide a method of extracting bacteria and the like from iiuid media for the production of biologicals as well as for various scientific uses.
The foregoing and other objects are attained by contacting a fluid medium containing bacteria or the like with a relatively inert, dielectric material which has been or which is subjected to a source of high potential, direct current electricity. This may be accomplished for example by passing a fluid such as water containing bacteria through a bed or column or a granular dielectric material to which is applied a high tension direct current by means of suitable electrodes. These electrodes are conveniently located at the top and bottom of the bed or column of the granular material. The dielectric material may be in the form of pellets, rods, tubes, etc., as Well as in the granular form.
Although our process may be conducted in any suitable apparatus, the apparatus as shown in the accompanying drawing has been found tov out, the apparatus being shown partially in cross;
section.
Figure 2 is the same type view as Figure 1 but is a slightly different form of apparatus which is adapted for our process.
The construction of the apparatus as well as the understanding of the operation of our process will be apparent from the following:
A suitable vessel or container I is preferably constructed of glass, porcelain or, if constructed with metal, it is preferably lined with glass, rubber or porcelain. An electrode, preferably a platinum electrode, 3 is placed near the top of vessel I and it extends either a short distance or substantially entirely across the vessel. A similar electrode 5 is inserted near the bottom of the vessel I. The electrodes 3 and 5 are suitably insulated from the vessel I if the latter is metallic. A high tension direct current potential is applied to the electrodes. 3 and 5 by any suitable means. Preferably the electrode near the top of the vessel I is made the anode while the electrode near the bottom of the vessel I is made the cathode. The electrodes 3 and 5 may be in the form of a wire or rod, or they may be in the form of a screen or foraminous plate which partly or completely covers the horizontally cross sectional area of the vessel I. A feed conduit 1 is connected into the top of vessel I while an outlet conduit 9 is connected into the bottom of vessel I. Both conduits 'I and 9 may be constructed of materials similar to those specified for vessel I.
A relatively thin layer of glass Wool II may be placed in the bottom of the vessel I and on top of the glass wool a granular material I3 is well packed in order to avoid the channeling of the fluid passing through the apparatus. On the top of the granular material I3 another layer of glass wool I5 is placed and this in turn is followed by a layer of glass beads I1. Optionally, an overflow pipe I9 is connected intothe top of the vessel I.
Water or other iiuid containing bacteria flows in through conduit l down through the granular material in vessel I and out through conduit 9. During the passage of the water a high tension direct current potential is applied to electrodes 3 and 5. The eiliuent flowing from conduit 9 has a substantially lower bacterial content than the feed which ilows'in through conduit l.
In Figure 2, container I is shown as a relatively shallow vessel as compared to vessel I, Figure 1 where the vessel is represented as a relatively long column. The feed pipe 'l in Figure 2 is connected with a perforated distributor conduit 8 which may be formed into a circle. The container I is provided with an ,outlet conduit 9. In Figure 2, electrodes 2I and 23 are inserted into the side of container I preferably diametrically opposite each other. A supporting screen, grate or other foraminous support is placed in the bottom of container i. On top of the support 25 a layer or glass wool li is placed followed by` well packed granular material i8 and this in turn is followed by another layer of glass wool Il on top of which is a layer of glass beads Il. The operation o! the apparatus shown in Figure 2 is apparent from the description of the operation of the apparatus in Figure 1. The container I conduits 1, I, and l and support 2l may be constructed of metal. porcelain. glass, synthetic resin. or many other 'desired materials. If metal be used, it is preferable that it be lined with glass, porcelain or rubber.
The following examples in which the proportions are in Darts by weight except as4 otherwise indicated are given by way of illustration and not in limitation. In order to demonstrate the high efiiciency of our invention, we have used uids contaminated with bacteria to an extremely high degree. It is apparent that the eiiiciency of removing bacteria from a fluid medium would be greater with a more prolonged contact with the fluid and the granular material which have been subjected to a high tension direct current potential.
Example 1 A glass column about V4" in diameter and 24" long is provided with two platinum electrodes about 19" apart. Each electrode consists of No. 22 gauge platinum wire and extends inside of the glass column a distance of about t". The electrodes are preferably relatively small in order to reduce the current density in the column as much as possible. Since our invention deals with the application of the high potential to the column of granular material but not to the passage of high currents of electricity: through the column, it is to be noted that the current density employed according to our invention is insumcient to actually kill the bacteria. In this invention the top electrode is the anode although our invention contemplates the use of the anode at either the bottom or top of the column. However, it is preferable t have the anode at or near the top of the column as somewhat better results are obtained than if the positions of the anode and cathode be reversed. This is of course based upon the direction of iiow being from top to bottom. We have found that the number of bacteria appears to be considerably greater in the vicinity of the anode than at the cathode.
The glass column is packed with a granular material such as flne sea sand. The sea sand used in the following test was such that 98% by weight was within the range of No, 20 to 100 mesh. The sand is washed and ignited prior to being packed in the column. Just prior to the introduction of the sand into the column it is washed with distilled water until the pH of the eiiiuent is about 6.8 at 25 C. The entire apparatus is preferably steam sterilized at about 121 C. either before cr after the sand is placed in the column. sterilized water is passed through the sand to wash out any free contaminating material or free bacteria.
About 1 liter of a bacterial suspension containing about 500,000 colonies per cc. of B. coli was passed-through the column ata rate oi about 14 cc. per minute. The etiiuent was collected in about 100 cc. fractions and aliquot proportions were withheld for bacteriological plating purposes. About 1 cc. of each fraction, proportionately further diluted, was introduced into 25 cc. of nutrient agar in a Petri dish after which the from about 1 m. a. to about 1.5 m. a.
Samples of sand from three diiferent locations in the column were removed after the foregoing tests. The first portion was taken from the vicinity of the anode at the top of the column. The second portion was taken from the center of the column while the third portion was taken from the bottom of the column in the vicinity of the cathode. One gram of each sample was slurried in a 5 cc. portion of sterile water and the sand allowed to settle. After settling, 1 cc. of the water in every sample was pipetted out, diluted 1:100 and a 0.1 cc. portion used for plating purposes. A bacteriological examination showed that the first sample contained about 6,000,000 colonies per cc. of the water into which the sand was slurried. 'I'he second sample contained about 190,000 colonies per cc. while the third sample contained approximately no colonies of bacteria. This indicates that the bacteria have been removed from the feed solution and that they have not been destroyed by this procedure, but have been concentrated on the granular material.
We have also found that sand or other granular material will retain its enhanced activity for a period of time after the electrical potential has been removed. However, it is preferable that the potential be applied during the entire process.
Sand which is not chargedby an electrical potential removes a very small proportion of bacteria from a uid medium under similar conditions. In fact, if an aqueous suspension containing about 500,000 or more colonies of B. coli per cc. be passed through an uncharged column of sand the eilluent shows no substantial reduction in the bacterial content.
Example 2 A bacterial suspension of pyocyaneous containing about 320,000 colonies per cc. is passed through a column of sand prepared in accordance with Example 1. About 1 liter of the suspension is passed through it at a rate oi' about 14 cc. per minute and the eilluent is collected in about' 100 cc. fractions. These were diluted, in-
. cubated and examined bacteriologically in the manner described in Example 1. The following results were obtained.
Potential Current Bacterial Eiiluent Fractions Counts per vous in M. A. en Emuem u Sand has been found to be an extremely convement and economical material for use in our apparatus but other granular or powdered materials having similar properties may be employed. Such granular materials should be nonconductors or poor conductors of electricity, or, in other words, they should be dielectrics. Such materials should have a resistivity of at least 100,000 ohms/cm. cube. The granular materials should be substantially insoluble in the fluid to be treated, e. g., water, and they should be relatively rigid, that is to say, the particles should not collapse or ooalesce to form a mush or paste. It is preferable that the materials have at least some degree of porosity, that they be water resistant, and that they be wet readily by water or other iluids to be purified. In view of these requirements it is apparent that we can not employ metals in their free state for our purpose. Examples of substances which we may use are bauxite, calcium carbonate, calcium sulfate, aluminum oxide in any form, barium sulfate, magnesium carbonate, silicon carbide, calcium phosphate, the natural clays, quartz, glass, silica gels, diatomaceous earth, sodium aluminum silicate and other complex aluminum silicates,
dried insoluble proteinaceous materials, cellulose such as cotton, wood pulp, paper or cloth, etc. Substances which have cation activity are not as desirable as chemically inactive materials since there is a tendency for them to neutralize or counteract part or all of the effect introduced by the high tension electric potential.
It has been disclosed and claimed in the copending application of Robert Bowling Barnes, Serial No. 457,524, filed September 5, 1942, that anion active resins are highly eiective for removing bacteria from fluid media. In another copending application of the present inventors Serial No. 457,523, led September 5, 1942, a process is described and claimed which makes use of an electrical potential in contact with anion active resins as an improvement over the invention described in the forementioned application of Robert Bowling Barnes. It is possible to remove bacteria more eiiciently and with a shorter period of contact by employing a high electrical potential in conjunction with the anion active resins. Similarly, we have found that it is possible to remove bacteria very much more eilioiently and with a shorter period of contact if an electrical current is applied to sand or other relatively inert granular materials.
The mechanism by which the various processes described above extract, adsorb, occlude or otherwise withdraw bacteria from iiuid material is unknown to us at this time. Accordingly, we do not intend that our invention should be limited to any particular explanation expressed or implied.
A valuable feature of our invention is that the bacteria remain in contact with the granular material in a virulent condition. The bacteria may be removed from the granular material by washing with water or other fluids and if de sired they may be killed or rendered inactive by treating them with germicidal solutionsor bacteriostatic solutions or subjecting them to a high potential, high frequency discharge by subjecting them to ultra-violet radiations, etc. Thus, bacteria may be collected for use in the preparation of biologicals or for use in scientific studies.
Our bacterial suspensions contain only about 0.00005 g. per cc. of sodium chloride and, therefore, with the small current density employed suiiicient chlorine could not be formed to destroy any substantial number of bacteria. This was conrrned by tests with ortho-toluidine as an indicator. Furthermore, the use of ShiiIs reagent failed to indicate the presence of any aldehydic materials, which in turn might impart some germicidal action.
Instead of passing the fluid containing bacteria through a bed or column of granular; material which is or which has been subjected to a high tension direct current, the former may be agitated in a suitable vessel with a sufficient quantity of the granular material to achieve the desired result, said vessel containing electrodes to which va high potential is applied, or said granular material may have been previously subjected to a high electrical potential. Furthermore, our inventloncontemplates the use of any number of beds of granular material as well' as `dielectric material is preferably from about volts D. C. to about 2000 volts D. C. and even higher voltages may be employed if desired. The current density is preferably kept as low as possible in order to avoid undesired decomposition of any salts which may be present in the :duid medium or of the uid medium itself. Furthermore, if it be desirable to recover the bacteria. in a virulent condition, the current density should not be high enough to kill the bacteria.
Our invention is not limited to the purication of liquids such as water, but is applicable to the puriilcation of any liquid or gas. If gases are to be purified, such as for example, air, it is preferable that the granular material be maintained in a damp or a wet condition, thus for example, air may be bubbled through a column packed with granular material through which a high potential electrical current is applied either with the column being kept substantially full oi' water or with water trickling or being sprayed down over the surface of the granular material. Gases may also be passed over the granular material after rst being saturated with water vapor. If this method be employed it may be desirable to carry out the process at temperatures nging from room temperature up to about Our invention is especially adapted to the removal of bacteria carrying a negative charge although it is not limited thereto. However, the results of the removal of bacteria from fluid media is especially high in the case of negativel" charged bacteria such as B. coli and the like.
Obviously, many modifications and variations in the processes and compositions described above may be made without departing from the spirit and scope of the invention as deiined in the appended claims.
We claim: i
1. A process for removing bacteria from aqueous media which comprises activating a granular dielectric material by applying a direct electric current potential of about 100-2000 volts thereto, in the presence of an aqueous liquid by means of electrodes oi such size and so spaced that the current passing between such electrodes when liquid is present is insuilicient to kill bacteria in said last-mentioned liquid, and passing an aqueous medium containing bacteria through a bed of the resulting activated dielectric material.
2. A process which vcomprises passing an aqueous medium containing bacteria through a bed of a granular dielectric material which is activated by applying a direct` electric current potential of about 10D-2000 volts thereto, by means of electrodes of such size and so spaced that the c lrent passing between such electrodes when s d aqueous media is present is insuiiicient to lkill bacteria in said liquid.
3. A process as in claim 2 wherein the granular dielectric material is sand.
4. A process as in claim 2 wherein the aqueous medium contains B. coli.
5. A process which comprises passing an aqueous medium containing bacteria through a bed of a granular dielectric material which is activated by applying a direct electric current potential oi' about 10G-2000 volts thereto, by means of electrodes of such size and so spaced that the current passing between such electrodes when said aqueous media is present is insumcient to kill bacteria in said liquid, and collecting at least a portion of the eilluent which contains a lower concentration of bacteria than said medium.
GARNET PHILIP HAM. ROBERT BOWLING BARNES.
REFERENCES crm-:D
The following references are oi record in the ille of this patent:
OTHER REFERENCES Turneaure et al., Public Water Supplies,
o Third Edition, copyrighted 1924, published by John Wiley 8: Sons, pages 426-429.
Falk, Electrophoresis of Bacteria, published in vol. II of Colloid Chemistry," by Alexander, 1928, by the Chemical Catalog Co., pages 738 and Austria June 25, 1937
US457522A 1942-09-05 1942-09-05 Process of removing bacteria from fluids Expired - Lifetime US2428328A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
US457522A US2428328A (en) 1942-09-05 1942-09-05 Process of removing bacteria from fluids

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
US457522A US2428328A (en) 1942-09-05 1942-09-05 Process of removing bacteria from fluids

Publications (1)

Publication Number Publication Date
US2428328A true US2428328A (en) 1947-09-30

Family

ID=23817067

Family Applications (1)

Application Number Title Priority Date Filing Date
US457522A Expired - Lifetime US2428328A (en) 1942-09-05 1942-09-05 Process of removing bacteria from fluids

Country Status (1)

Country Link
US (1) US2428328A (en)

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US2555487A (en) * 1948-02-27 1951-06-05 United Shoe Machinery Corp Chromatographic process and apparatus
US2573967A (en) * 1947-05-01 1951-11-06 Us Hoffman Machinery Corp Electrical precipitation method
US3058894A (en) * 1959-08-10 1962-10-16 Columbian Carbon Treatment of microorganisms
US3365858A (en) * 1966-10-20 1968-01-30 Universal Oil Prod Co Combined heat interchanger and electrostatic precipitator
US4732185A (en) * 1985-05-21 1988-03-22 Baremek Pty. Limited. Electrophoretic cleaner and sterilizer
US4838154A (en) * 1985-05-31 1989-06-13 Maxwell Laboratories, Inc. Apparatus for extending the shelf life of fluid food products
US4886593A (en) * 1986-09-11 1989-12-12 Gibbs Robert W Device for destroying bacteria
US5185086A (en) * 1991-07-16 1993-02-09 Steven Kaali Method and system for treatment of blood and/or other body fluids and/or synthetic fluids using combined filter elements and electric field forces
US5447733A (en) * 1994-01-06 1995-09-05 Purepulse Technologies, Inc. Prevention of electrochemical and electrophoretic effects in high-strength-electric-field pumpable-food-product treatment systems
US20030049233A1 (en) * 2001-07-18 2003-03-13 Medra, Inc. Embryonic stem cells, clinical applications and methods for expanding in vitro

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE65846C (en) * H. ROESKE in Philadelphia, V. St. A., Chestnut Street 501 Device for conducting electrical currents through the water of open filter systems
US517499A (en) * 1894-04-03 Process of filtering or purification of liquids
US1738801A (en) * 1926-12-02 1929-12-10 Reuben B Shemitz Apparatus for and process of detecting and segregating bacteria in liquids
US1992974A (en) * 1931-03-18 1935-03-05 Thompson Engineering Company Electrostatic precipitator
AT149966B (en) * 1927-12-22 1937-06-25 Paul Ing Schiessler Process for disinfecting and clarifying coarse colloid or molecularly disperse systems in the electrostatic field.
US2297601A (en) * 1940-09-03 1942-09-29 American Air Filter Co Electric gas cleaner

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE65846C (en) * H. ROESKE in Philadelphia, V. St. A., Chestnut Street 501 Device for conducting electrical currents through the water of open filter systems
US517499A (en) * 1894-04-03 Process of filtering or purification of liquids
US1738801A (en) * 1926-12-02 1929-12-10 Reuben B Shemitz Apparatus for and process of detecting and segregating bacteria in liquids
AT149966B (en) * 1927-12-22 1937-06-25 Paul Ing Schiessler Process for disinfecting and clarifying coarse colloid or molecularly disperse systems in the electrostatic field.
US1992974A (en) * 1931-03-18 1935-03-05 Thompson Engineering Company Electrostatic precipitator
US2297601A (en) * 1940-09-03 1942-09-29 American Air Filter Co Electric gas cleaner

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US2573967A (en) * 1947-05-01 1951-11-06 Us Hoffman Machinery Corp Electrical precipitation method
US2555487A (en) * 1948-02-27 1951-06-05 United Shoe Machinery Corp Chromatographic process and apparatus
US3058894A (en) * 1959-08-10 1962-10-16 Columbian Carbon Treatment of microorganisms
US3365858A (en) * 1966-10-20 1968-01-30 Universal Oil Prod Co Combined heat interchanger and electrostatic precipitator
US4732185A (en) * 1985-05-21 1988-03-22 Baremek Pty. Limited. Electrophoretic cleaner and sterilizer
US4838154A (en) * 1985-05-31 1989-06-13 Maxwell Laboratories, Inc. Apparatus for extending the shelf life of fluid food products
US4886593A (en) * 1986-09-11 1989-12-12 Gibbs Robert W Device for destroying bacteria
US5185086A (en) * 1991-07-16 1993-02-09 Steven Kaali Method and system for treatment of blood and/or other body fluids and/or synthetic fluids using combined filter elements and electric field forces
US5447733A (en) * 1994-01-06 1995-09-05 Purepulse Technologies, Inc. Prevention of electrochemical and electrophoretic effects in high-strength-electric-field pumpable-food-product treatment systems
US20030049233A1 (en) * 2001-07-18 2003-03-13 Medra, Inc. Embryonic stem cells, clinical applications and methods for expanding in vitro

Similar Documents

Publication Publication Date Title
US2428328A (en) Process of removing bacteria from fluids
US4430226A (en) Method and apparatus for producing ultrapure water
GB1013069A (en) Process and apparatus for treating fluids
US3766034A (en) Removal of ions from liquids
US3770625A (en) Removal of virus from fluids
US4045553A (en) Method of treating silver impregnated activated carbon
US2399289A (en) Apparatus for purifying liquids
RU2110482C1 (en) Method and apparatus for controlled sorption of soluble organic substances and heavy metal ions from aqueous solution
US2701792A (en) Treatment of aqueous liquids with bacteriostatic carbon
FR2599758B1 (en) PROCESS AND INSTALLATION OF PERCOLATING ELECTROLYSIS THROUGH ONE OR MORE POROUS VOLUME ELECTRODES
US1782850A (en) Method of purifying water and apparatus therefor
TW365540B (en) A method for the removal of viruses from protein solutions by adsorption using solid phase suspension particles
US2374805A (en) Sterilization of water for drinking purposes
US2247711A (en) Sterilization of liquids
IL28070A (en) Removal of colloidal materials from aqueous liquids
US2210966A (en) Purification of potable water
RU2137717C1 (en) Method of removing copper ions from waste waters
GB1374006A (en) Separation of a liquid containing charged particles or and polarizable molecules
JPS6422393A (en) Water cleaning device
RU2099803C1 (en) Method and device for cleaning process and natural water from radionuclides
US2540223A (en) Sterilization of liquids
JP2769359B2 (en) Filter material between gravel
Minz Some results of research into drinking-water purification and disinfection
US2214649A (en) Flushed electrical precipitator
US2072376A (en) Process of removing fluorides from water